The Reaction of Ozone with Ammonia

deposited on the cell walls and windows, appeared almost immediately and remained even ... [ N H 3 ]/[O 3 ] 0. = 625 fits the three-half order law wel...
1 downloads 0 Views 2MB Size
6 The Reaction of Ozone with Ammonia KENNETH J. OLSZYNA and JULIAN HEICKLEN

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

Department of Chemistry and Center for Air Environment Studies, The Pennsylvania State University, University Park, Pa. 16802 Mixtures of O and excess NH react at ~ 30°C to produce O , H O, N O, Ν , and solid ΝΗ ΝO . The amounts of the gas-phase products, relative to the ozone consumed, are 1.05, 0.31, 0.032, and 0.031, respectively. Neither H nor NH NO was produced. For [NH ]/[O ] ratios < 50, the disappearance rate of O was first order in [O ] and increased slowly with increasing [NH ]/[O ] to an upper limiting value of 0.21 min , where [O ] is the initial pres­ sure of O . As the reaction proceeded and the [NH ]/[O ] ratio passed 120 (or if [NH ]/[O ] > 120), the rate shifted to three-halves order in [O ] and was proportional to [NH ]- . The reaction is interpreted as a chain mechanism with the heterogeneous decay of O as the initiating step. Nitrogenous products come from oxidation of HNO with O , followed by reaction with NH . 3

2

2

3

2

2

4

3

2

4

2

3

3

0

3

3

3

-1

3

3

0

0

3

3

3

3

3

0

3

3

1/2

3

3

3

T h e room-temperature photooxidation of N H has been studied by several workers, and the results have recently been reviewed (1). The products of the reaction are H , N , H O, and NH NO . Bacon and Duncan (2) reported that the overall reaction is approximately repre­ sented by the expression 3

2

2

2

4

3

8NH + 7O --> 2N + 2NH NO + 8H O 3

2

2

4

3

2

Apparently the only study of the ozonation of N H was done by Strecker and Thienemann, and they found that the products are H 0, 0 , NH4NO3, and N H N 0 (3). They reported the overall stoichiometrics to be 3

2

4

2

2

2NH + 40 -> 40 3

3

2

2NH + 30 -> 30 3

3

2

+ H 0 + NH4NO3 2

+ H 0 + NH N0 2

4

2

Because of the lack of data on the O3-NH3 reaction and because both gases are significant impurities in urban atmospheres, we reinvesti191 In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

192

PHOTOCHEMICAL

SMOG

AND

OZONE REACTIONS

gated this system. W e analyzed the products and made kinetic measure­ ments. The results are reported below. Experimental

Most of the gases used were from the Matheson Co.; these included extra dry grade 0 , C. P. grade N H , and prepurified H . The ultra pure grade helium was used after passing through a filter containing glass wool, Drierite, and Ascarite. The N H was distilled from —100° to —196°C; the 0 and H were used after passing through traps at —196°C. The only detectable impurities were 0.05% N i n the 0 , < 0.01% air in the H , and none ( < 0.01% ) in the N H . Ozone was prepared from a tesla coil discharge through 0 . The ozone was triply distilled at —186°C and collected at —196°C with continuous degassing. The ozone, hydrogen, and oxygen pressures were measured by an H S 0 manometer; the 0 pressure was checked by optical absorption at 2537 A . The N H and H e pressures were measured by an Alphatron Vacuum Gauge, M o d e l 820. The gases were introduced into the cell, and the reaction was monitored continually by ultraviolet absorption spectroscopy using low intensities so that photochemical reaction was not induced by the moni­ toring lamp, which was a Philips 93109E low-pressure mercury resonance lamp. The radiation passed through a Corning 7-54 filter to remove radiation below 2200 A and above 4200 A and a cell filled with chlorine to remove radiation above 2800 A before passing through the reaction vessel to a R C A 9-35 phototube. Some runs were monitored with radiation be­ tween 3000-4200A where neither 0 nor N H absorb; this spectral region was isolated by a Corning 7-54 filter and a glass plate. A l l gases were handled in a grease-free, high vacuum line using Teflon stopcocks with Viton Ό " rings. The reaction vessel was a quartz cell 5 cm long and 5 cm in diameter. To test the effect of surface area and volume, runs were done in the vessel unpacked, as well as packed with 1000 solid spherical glass beads (Kimax, 3 db 0.5 mm diameter). Adding the beads increased the surface area from 139 to 412 sq cm and reduced the volume from 102.3 to 88.1 cc. The beads were conditioned by ozone until the heterogeneous decay of pure ozone was the same as in the unpacked cell. In most of the experiments after the reaction was complete, the products were collected and analyzed by gas chromatography. Aliquot portions of the noncondensable gases were analyzed on an 8 ft long 5A molecular sieve column at 0°C with an H e flow rate of 94 c c / m i n . The condensable gases were distilled from —100° to —196 °C and then from - 1 3 0 ° to - 1 9 6 ° C . The residue from the - 1 0 0 ° C distillation and the distillate from the —130 °C distillation were separately passed through a Porapak Τ column 8.5 ft long operated at 79-82 °C and a H e flow rate of 140 c c / m i n . F o r both fractions a G o w M a c M o d e l 40-012 voltage regulator with a thermistor detector was used with a 1-mv recorder. The solid product of the reaction was identified by infrared spec­ troscopy ( I R ) . The reaction was carried out in a borosilicate glass cell 6 cm long and 2.1 cm in diameter with N a C l windows but using higher 2

3

2

3

2

2

2

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

2

2

3

2

2

4

3

3

3

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

6.

OLSZYNA AND

193

Reaction of Ozone with Ammonia

HEiCKLEN

0 pressures and [ N H ] / [ 0 ] 0 ratios from 5-12. "When N H was added to the borosilicate glass cell containing ozone, a white aerosol, which deposited on the cell walls and windows, appeared almost immediately and remained even after the cell was evacuated. However for [ O ] ^ 10 Torr, an explosion resulted when N H was added. 3

3

3

3

3

0

3

Results When N H is added to 0 in the reaction vessel, the 0 is consumed, and a white solid aerosol is produced which settles on the cell walls. The 0 consumption is monitored by its intense absorption at 2537 A . For a freshly cleaned cell some decay of the 0 occurs even in the absence of N H . However the reaction with N H is much more rapid but is not reproducible. As the solid deposit accumulates from several runs, the background reaction becomes negligible, and the reaction with N H becomes slower and reproducible. A l l reported results here are for the cell (packed and unpacked) conditioned this way. The light monitoring the 0 was too weak to cause photodissociation to occur significantly. This was checked by doing duplicate runs with continuous or intermittent radiation; decay curves were the same. Ozone decay curves were obtained for initial ozone pressures, [ O ] , of 0.14-3.02 Torr, initial N H pressures of 0.36-292 Torr, and [ N H ] / [ O ] ratios of 0.9-649. The decay curves were tested for the reaction order in [ 0 ] . The order depended only on the ratio [ N H ] / [ 0 ] and varied between 1-1.5. For three runs at [ N H ] / [ O ] of 10.5, 50, and 625 the first and three-halves order plots are shown in Figures 1 and 2, respectively. The results in Figure 1 show that at low [ N H ] / [ 0 ] ratios ( [ N H ] / [ O ] = 10.5), a good first-order decay plot is obtained for at least 8 1 % decomposition. In Figure 1 the ordinate scale for curve A is on the right for clarity; the numbers by the data points indicate percent 0 decomposed. A t an [ N H ] / [ O ] ratio of 50, the curve starts to give a first-order plot but falls off from linearity above 6 0 % decomposition where [ N H ] / [ 0 ] becomes large ( > 120). For an [ N H ] / [ O ] ratio of 625, the first-order plot has no linear region. The same three runs are shown in Figure 2 on a three-halves order plot (ordinate scale on right for clarity; numbers by data points indicate % 0 decomposed). The run at [ N H ] / [ O ] = 10.5, which showed good first-order behavior, does not give a linear 3/2-order plot. The run at intermediate [ N H ] / [ O ] does not fit 3/2-order initially, but after about 7 0 % decomposition when [ N H ] / [ 0 ] ,— 150, the 3/2-order plot becomes linear. The run with [ N H ] / [ O ] = 625 fits the three-half order law well to at least 88% decomposition. A l l of our runs showed the same behavior which can be summarized as follows. 3

3

3

3

3

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

3

3

3

3

3

3

3

3

3

3

3

3

3

0

3

0

3

3

0

3

0

3

3

3

3

0

3

3

3

0

3

3

3

0

3

3

0

3

3

3

3

0

-d[0 ]/dt = k[0 ] -d[O ]/dt = &'[0 ] 3

z

3

3

3/2

[NH ]/[0 ] < 50 [NH ]/[0 ] > 120 3

3

3

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

(a) (b)

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

194

PHOTOCHEMICAL

0

Figure 1.

2

4

6

8

TIME

, MINUTES

SMOG

10

A N D OZONE REACTIONS

12

14

First-order plots of the ozone decay in the NH -0 reaction at room temperature in the unpacked reaction vessel 3

3

It should be realized that the coefficients k and k' are functions of [ N H ] which remained nearly constant during any run. These coefficients are listed i n Table I for the unpacked reaction vessel and i n Table II for the reaction vessel packed with 1000 glass beads. After the optical density no longer changed, the cell was evacuated, and the gases were analyzed. The optical density d i d not change upon evacuating the cell but was slightly higher (0.01-0.04) than before the runs because of the absorption of the solid which d i d not pump away. Periodically the cell was cleaned by introducing about an atmosphere of N H which removed the solid and reduced the absorbance. The decay curves were corrected for this residual absorbance i n computing rate coefficients. The optical attenuation resulting from the solid was more clearly shown by monitoring some runs with radiation between 3000-4200 A (principally 3660 A ) , where the 0 absorption is unimportant. Some results are shown i n Figure 3. Initially the optical attenuation increases to a maximum as the aerosol is formed and then drops as the aerosol deposits 3

3

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

6.

OLSZYNA A N D

HEicKLEN

Reaction of Ozone with Ammonia

195

on the wall. The results are similar in the unpacked and packed cell. The presence of excess H e (not shown) also hardly affects the results. The increase i n optical attenuation is most marked when [ N H ] and [ O ] are large; however, correcting the decay plots is unimportant because the 0 absorbance is also large. If [ N H ] and [ O ] are low, the aerosol interference is negligible (presumably because of more rapid settling on the walls ). Optical attenuation because of the aerosol only interferes with the 0 decay curves for high [ N H ] / [ O ] . The solid product was identified as N H N 0 by IR by performing some runs i n cells with N a C l windows and pumping away the residual gases. The infrared spectrum showed the strong, broad absorption in the 3.03-3.30/x (3300-3030 cm" ) region resulting from N H stretching vibrations of the N H ion and the strong, broad N H bending band near 7.00,* (1429 cm" ). The weak, sharp absorption near 11.50-12.00,* (870-833 cm" ), which is the stretching of the single bond of the N O linkage i n the N 0 " ion, is also present (4). The two strong N = 0 stretching bands in the 5.95-6.06,* (1680-1650 cm" ) and 6.16-6.21/* (1625-1610 3

3

3

3

3

3

3

0

0

4

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

3

3

1

4

+

4

+

1

1

3

1

TIME , MINUTES

Figure 2. Three-halves order plots of the ozone decay in the NH -0 reaction at room temperature in the unpacked reaction vessel 3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

3

0

196

PHOTOCHEMICAL

SMOG

Table I. [O.]o,

[NH ]/[0*]o

Torr

Torr

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

t

0.9 1.2 1.8 1.85 2.8 3.4 3.9 4.3 4.4 5.0 6.1 6.5 7.0 8.3 13.1 13.6 14.6 15.2 16.6 18.1 21 22 22 22.7 23.1 23.6 30 30 35 45.6 44.1 50 51.6 75 80 80 88 93 118 119 130 495 649 a

a 6

0.39 1.52 0.20 0.62 0.39 0.81 0.79 0.14 1.44 1.14 0.78 1.23 1.03 0.78 3.02 0.99 2.06 1.80 1.49 0.75 1.29 0.40 1.66 2.08 0.99 0.34 0.83 1.63 1.46 0.79 1.43 0.48 0.45 1.37 0.47 1.58 0.86 0.89 0.44 0.38 0.66 0.43 0.45

0.36 1.8 0.36 1.15 1.1 2.8 3.1 0.61 6.6 5.7 4.8 7.9 7.2 6.5 39.5 13.4 30.1 28.3 25.9 13.6 27 8.7 38 47.1 22.8 8.1 25.6 4.8 52.1 36.0 63.0 24.1 23.3 102 37.5 128 76 83 53 45 86 213 292

Temp, °C 32.3 28.1 31.5 26.4 31 27.9 30 31 26.8 — 28.2 — — 31.5 30 32.0 30 32 26.7 31.9 31.9 33.8 32.4 24.3 — — 31 — 27.0 31.0 30.6 24.8 29.9 33.2 30.8 28.5 29.2 31 26.8 26.2 30.5 27.0 26.3

AND

OZONE

REACTIONS

Reaction of N H w i t h 3

mmr

1

0.084 0.106 0.106 0.083 0.105 0.125 0.125 0.126 0.141 0.141 0.143 0.149 0.160 0.178 0.184 0.185 0.197 0.203 — 0.195 0.202 0.183 0.210 — — — 0.193 0.214 0.188 0.202 ~0.23 — ~0.22 ~0.30 ~0.23 ~0.24 ~0.19 ~0.25 — — — — —

Torr' / 1

2

— — — — — — — — — — — — — — — — — — — — — — — — — — — — — — 0.37 — 0.77 0.26 0.58 0.24 0.29 0.34 0.33 0.34 0.30 0.39 —0.45

0 decay not monitored; monitoring lamp off. Excludes runs with [NH ]/[0 ]o >100 3

3

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

min

6. 0

3

OLSZYNA

A N D

Reaction of Ozone with Ammonia

HEiCKLEN

i n the Unpacked Cell [0 ]/[0,] 0

[N ]/[Os] 0

[H 0]/[Os] 0

[N 0]/[Os] 0

0.94 1.11 0.96 1.13 0.99 1.12

0.031 0.020 0.038 0.037 0.040 0.023

— 0.30 — 0.19 — 0.29

— 0.026 — 0.030 — 0.039

1.09 1.03 1.11 1.05 1.05

0.019 0.019 0.024 0.020 0.021

0.28 — 0.32 — —

0.030 — 0.041 — —

1.06 1.03

0.020 0.024

— —

— —

1.11

0.027

0.32

0.029

1.04 1.06 1.03 1.05 1.11 1.08

0.028 0.033 0.031 0.034 0.033 0.044

— — — 0.33 0.37 0.29

— — — 0.023 0.033 0.041

1.00 1.16

0.036 0.041

— 0.36

— 0.026

1.07

0.049

0.31

0.041

1.00

0.043





1.09 1.00

0.020 0.040

0.31 —

0.027 —

1.05 1.14 1.00 1.01 1.11

0.058 0.062 — 0.077 0.086

0.35 — — 0.36 —

0.044 0.052 — 0.047 0.055

0.31 ±0.03

0.032 ±0.006

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

2

Ave. =

1.05 =1=0.05

2

0.031 =1=0.008

6

2

2

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

6

198

PHOTOCHEMICAL

SMOG

AND

OZONE REACTIONS

cm" ) regions, which indicate nitrites, are absent. The nitrite absorption bands are among the strongest observed i n IR spectra (4). Thus our re­ sults suggest the absence of N H N 0 , contrary to the findings of Strecker and Thienemann (3). The infrared spectrum obtained here agrees well with the Sadtler standard spectrum of NH4NO3 except for the strong, sharp peak at observed by us, which may result from adsorbed O H . Although the O - H stretching vibration normally occurs at lower wavelengths (2.9/*), the O H bond is sufficiently weakened during adsorp­ tion so that the O H stretching band could be raised to 3Λμ (5). The gaseous products were 0 , N , H 0 , and N 0 . W e looked for H , but it was absent. The major gaseous products were 0 and H 0 . Their relative amounts, compared with [ O ] , are listed in Table I for the unpacked reaction vessel. Their values do not vary with reactant pressures, and their average values and mean deviations are 1.05 ± 0.05 and 0.31 ± 0.03, respectively, for [ O ] / [ O ] and [ H O ] / [ O ] . The minor products, N and N 0 , deviate more. For [ N H ] / [ O ] < 100, the relative values are reasonably constant and are 0.031 ± 0.008 and 0.032 ± 0.006, respectively, for [ N ] / [ O ] and [ N O ] / [ O ] ; for [ N H ] / [ O ] > 100, both quantities are larger. 1

4

2

2

2

2

2

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

2

2

3

2

2

3

3

0

2

2

3

3

2

3

2

0

3

0

3

0

0

2

3

0

0

Table II.

The Reaction of 0

3

with N H

3

in the Packed Cell

[NH,]/[0 ]o

[O,]o, Torr

[NHz], Torr

Temp, °C

k, min-

1.6 2.0 7.5 7.9 8.1 8.4 9.3 27.3 48 146

0.84 0.42 0.44 0.78 0.26 0.78 1.68 0.60 0.79 0.80

1.3 0.8 3.3 6.1 2.1 6.5 15.7 16.3 37.6 118

30 30.5 31 31 31 31 30 30.5 31 31

0.147 0.189 0.224 0.205 0.242 0.210 0.220 0.230 0.262 0.485

3

1

a

° 3/2-order rate constant. Units are Torr ' min . -1

2

-1

The first-order rate coefficients, h, listed in Tables I and II increase with the ratio [ N H ] / [ O ] as shown i n Figure 4 but otherwise do not depend upon [ N H ] or [ O ] . For any value of [ N H ] / [ O ] the coefficients are larger in the packed than in the unpacked cell, showing heterogeneous effects, k can be fitted to the expression (see Figure 5). 3

3

3

0

3

0

3

* ^ = α + β[Ο,] /[ΝΗ,] 0

3

0

(c)

where a and β are, respectively, 22 and 144 sq min for the unpacked cell and 16 and 38 sq min for the packed cell.

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

6.

OLSZYNA AND H E i C K L E N

199

Reaction of Ozone with Ammonia

The 3/2-order coefficient k' drops from 0.77 to 0.24 T o r r " m i n as [ N H ] increases from 23.3 to 128 Torr. A t higher N H pressures, k! increases with [ N H ] . k' at the two highest N H pressures may increase as a result of the sizeable effect of the aerosol attenuation at high [ N H ] / [ O ] and as a result of diffusion effects. The aerosol effect was so important in the packed cell (because of the larger rate coefficients) that only one reliable value for k' could be obtained, and its value of 4.85 T o r r " min" was larger than in the unpacked cell for similar [ N H ] / [ O ] ratios. 1/2

3

- 1

3

3

3

3

3

0

172

3

3

1

0

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

Ο.ΙΟ r 3-10

"3J

Torr

Torr

PACKED

CELL

143

1.5

214

17.6

1.5

26.4

610

0.4 UNPACKED

244 CELL

145

1.4

14.7

1.5

203 22

485

0.4

193

Figure 3. Plot of the change in optical density at 3000-4200A (mainly 3660A) vs. reaction time for several runs in the unpacked and packed reaction cell. At these wavelengths the reactants do not give measurable absorption. The change in optical density is caused by aerosol formation.

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

200

photochemical

smog

a n d ozone

reactions

.28 .26 .24 .22 .20 .18

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

.16 .1 4 .12 .10 .08 .06

PACKED

UNPACKED

CELL

CELL



Δ 0.0-05



Ο 0.5-1.0

TORR [0g]

0

a

A

1.0-2.0

TORR [ 0 ]

0



2.0-3.0 TORR [ 0 ]

0

TORR [ 0 ] 3

3

3

0

.04 .02

J

I

5

[

I I I '

10 N H

50

100

J/[°Jo

Figure 4. Semilog plots of the first-order rate constant, k, vs. [ N H ] / [ 0 ] in the unpacked and packed reaction cell 3

3

t

Some runs were done with other gases added (see Table I I I ) ; two runs were done with the major product, 0 , added to see if it influenced the reaction. The amount of 0 was comparable with that produced i n a run. It d i d not affect the order of the reaction, the value of the rate coefficient, k, or the relative amounts of the other gaseous products. Two runs were done with H added. One was with a small amount of H , which did not influence the reaction, to see if the H would be recovered. It was completely recovered after the run, showing that our finding of no H production was correct; any H would have been detected if formed. The other run had 850/x of H added. In this case some of the H was consumed, and the production of 0 was enhanced. Several experiments were done i n the unpacked and packed vessel in the presence of a large excess of H e to test for inert gas effects. The [ N H ] / [ 0 ] o ratios varied from 1.5-23, and all the decay curves obeyed first-order kinetics. The relative gaseous product yields were essentially unaffected i n the unpacked cell (products were not analyzed i n the 2

2

2

2

2

2

2

2

2

3

2

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

6.

201

Reaction of Ozone with Ammonia

OLSZYNA AND H E i C K L E N

packed cell), except possibly [ O ] / [ O ] dropped slightly. However the rate coefficients k were reduced as the H e pressure was raised, but the effect was more pronounced in the unpacked cell. The results with H e are graphically shown in Figure 6 where (ko/k) is plotted vs. [ H e ] . In this plot k is the first-order decay coefficient with H e present, and ko is the first-order decay coefficient for H e absent as determined from Figure 5 at the same value of [ N H ] / [ O ] . The plot is quite linear for the unpacked cell and reasonably linear for the packed cell. The values of k /k are functions of [ H e ] and not functions of [ H e ] / [ N H ] , an unexpected observation (See Discussion). The rela­ tionship is 2

3

0

2

3

3

0

0

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

3

(ko/k)*

1 +

=

γ [He]

(d)

where γ is 0.0140 and 0.0055 Torr" , respectively, for the unpacked and packed cell. 1

Discussion

The results give a complex rate law but a simple dependence for the forming of products. The major gaseous products, 0 and H 0 , are formed i n the same relative amounts i n each experiment, and N and N 0 are reasonably independent of conditions, at least for [ N H ] / [ O ] 2

2

2

2

3

0.4

0.6 [03] /[NH ] 0

Figure 5.

3

3

Plot of k" vs. [O ~\ /[NH ~\ in the unpacked and packed reaction cell 2

3

0

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

0

202

PHOTOCHEMICAL

SMOG AND OZONE REACTIONS

Table III. [X], Torr

3

with

Temp,

[Odo, Torr

[NHi]/[0*]o

The Reaction of 0

Torr

X = 0 , Unpacked Cell 0.93 12.8 1.62 32.6 X = H , Unpacked Cell 21.7 1.11 24.1 1.00 29 29 X = He, Unpacked Cell 16.7 1.48 24.9 22 0.71 16 —12 0.46 —5.5 23 0.72 16.9 15.6 1.52 23.8 15 0.81 12 18 1.63 29.5 —20 0.41 —8

°C

min*

29.4 29.0

0.152 0.180

31.1 32.8

0.191 0.202

29.2 28.4 27.9 26.5 28.2 29.0 28.0 27.5

0.151 0.105 0.064 0.063 0.066 0.048 0.048 0.036

— — — — — — — — — —

0.136 0.135 0.140 0.074 0.091 0.090 0.110 0.099 0.110 0.094

1

2

1.30 2.10

13.6 20.1

2

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

0.014 0.850

e b

66 161 380 445 546 785 1058 1300

180 195 225 815 824 844 855 880 900 925 1

100%

7.9 8.8 9.6 —1.5 8.8 8.0 22.2 9.5 23.0 7.6 of

X --= He, Packed Cell 0.43 3.4 0.81 7.1 1.60 15.4 0.44 4 0 3

+ H 0 +

2

2

NH N0 4

3

The 0 produced was equal to, or slightly greater than, the 0 consumed. This suggests that whenever an 0 reacts, 0 must be a product; this inference w i l l greatly limit mechanistic possibilities. The above stoichiometric equation predicts [ H O ] / [ O ] = 0.25, but we observed 0.31 ± 0.03. The additional H 0 is associated with the production of the minor products N and N 0 . The rate law is more complex. Two results give evidence for a free radical chain mechanism. The more compelling is the non-integral order of the reaction under some conditions—i.e., 3/2-order at [ N H ] / 2

3

3

2

2

3

0

2

2

2

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

6. NH

203

Reaction of Ozone with Ammonia

OLSZYNA AND H E i C K L E N

in the Presence of Added Gases

3

[0 ]/[0 ]o 2

[N ]/[0,] t

3

[H0]/[O,)

0

[NJ)]/[0,]o

O

X = 0 Unpacked Cell 0.028 — 0.040 0.31 X = H , Unpacked Cell 2

— —



0.026

2

— —

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

1.04 1.30

— —

— —

X = He, Unpacked Cell 0.028 — 0.030 0.38 0.043 0.35 0.042 0.30 0.030 0.34 0.024 0.35 0.044 0.33 0.065 —

0.94 0.85 1.00 0.87 0.85 0.96 1.08 1.07



0.038 0.039 0.034 0.020 0.030 0.019 0.035 0.031 ±0.007

0.038 0.34 =±=0.010 ±0.02 X = He, Packed Cell

0.95 ±0.08





— —



b



70% of H2 recovered at end of run.

[O3] > 1^0; the other evidence is the experiment with 850/A of H added. Some of the H was consumed, indicating an intermediate that readily attacks H at room temperature; such an intermediate is the H O radical. Further evidence for H O is that [ O ] / [ O ] is much greater i n the presence of H . This occurs when H O attacks H to produce H , which would then react with 0 to produce excited H O which induces the chain decomposing of 0 to produce 0 (6). 2

2

2

2

3

2

0

2

3

3

2

Other results indicate the importance of wall reactions. First is that k depends on [ O ] . It is unusual for a rate coefficient to depend on the initial concentration of a reactant when that reactant is entirely consumed in the reaction. A similar result was found in the 0 — C S reaction where wall reactions were also indicated (7). The importance of wall reactions was confirmed by the experiments in the packed reac3

0

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

2

PHOTOCHEMICAL

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

204

0 I 0

SMOG A N D OZONE REACTIONS

I

I

I

ι

200

400

600

800

1

1000

1

1200

[He] , Torr Figure 6. Plot of the square of the ratio of the rate constant in the absence of He, k , to that in the presence of He, k, vs. the He pressure in the unpacked and packed reaction cell (the values for k were taken from Figure 5 at the values of [ 0 ] / [ N H ] cor­ responding to each k) 0

0

3

0

3

tion vessel where the rate coefficients were larger for conditions com­ parable with those in the unpacked cell; under some conditions k was 6 0 % larger. Also supporting wall reactions is the experiments in excess H e . H e , an inert gas, reduces the rate coefficient which indicates that either the chain termination steps require a chaperone gas or that initiation is a diffusion-controlled wall reaction. Since the H e effect is much more pronounced i n the unpacked cell, the latter of the two possibilities is supported. To formulate a mechanism, it is necessary to use a reaction scheme that, 1. produces 0 whenever 0 reacts 2

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

6.

205

Reaction of Ozone with Ammonia

OLSZYNA AND H E i C K L E N

2. gives a free radical chain mechanism with H O being the prob­ able chain carrier 3. involves wall initiation The initiating steps are probably those of the heterogeneous decay of 0 which occurs even in the absence of N H . The predicted reaction steps are 3

3

wall 20

3

0 * + 0 2

3

->

20 + 0 *

(1)

->

20 + 0

(2)

2

2

0 + 0 -> 2 0 (3) where 0 * is an excited 0 molecule, possibly i n a singlet state. Reaction 1 occurs on the wall and is highly exothermic. It is not unreasonable to expect that some of the 0 produced is energized. The excited 0 pro­ duced could easily have enough energy to dissociate another 0 molecule. If singlet 0 is produced, Reaction 2 is well established (8). The Ο atom would react with 0 via Reaction 3 or i n the presence of N H ; it could also react via 3

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

2

2

2

2

2

2

3

2

3

3

Ο + NH

—> H O + N H

3

(4)

2

When H O is produced, the chain is propagated by HO + N H

3

-> H 0 + N H 2

(5)

2

The N H radical reacts readily with 0 , and since 0 the only exothermic reaction is 2

3

NH

+ 0 -> N H 0 + 0

2

3

2

2

must be produced, (6)

2

The chain carrier, H O , is probably regenerated by the reaction N H 0 + 0 -> H O + 0 2

3

+ HNO

2

(7)

One complication is the reaction of N H with 0 , a product of the reaction. Two possible reactions have been proposed for the N H - 0 interaction ( I ) 2

2

2

NH

2

+ 0 -> H 0 + N O

2

2

2

or NH

2

+ 0 -» HNO + HO 2

The former reaction is a chain terminating reaction and cannot be impor­ tant i n our system since the rate coefficient is unaffected even when 2.1 Torr of 0 was added. The latter reaction regenerates the chain and pro­ duces H N O and thus is similar to Reaction 7; however, it consumes 0 . If it were as important as Reaction 6, [ O ] / [ O ] should drop below unity. Either its rate constant is measurably smaller than that of Reaction 6, or the reaction proceeds through an intermediate complex which lives long enough to react with 0 , viz 2

2

2

3

0

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

206

PHOTOCHEMICAL

NH NH 0 2

+ 0 -> N H 0

2

2

+ 0

2

SMOG AND OZONE REACTIONS

2

(8)

2

N H 0 + 20

3

2

(9)

2

Reaction 8 followed by Reaction 9 is kinetically indistinguishable from Reaction 6. Termination probably occurs from the interaction of two N H 0 radicals since N H must be rapidly scavenged by either 0 or 0 . The reaction is represented as 2

2

3

2

2 N H 0 -> Termination

(10)

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

2

The products of the reaction are unimportant and undetectable in our system because Reaction 10 occurs infrequently. A n upper limit to Reac­ tion 10's importance is made by considering the following information. The ratio kjk± is about 75, discussed below, but even at [ N H ] / [ 0 ] — 1, [ 0 ] / [ 0 ] o •— 1.0, which indicates that Reaction 4 leads ulti­ mately to the bulk of 0 decomposition. The chain lengths must be large—i.e., ^ 500; also four 0 molecules are consumed in each chain cycle. Therefore any product from Reaction 10 has a final concentration < 5 X 10" [O ]o, which would be undetectable. Nevertheless we can speculate about Reaction 10. For example, the isomeric H N O H form of N H 0 possibly is involved and reacts with itself to produce N -f2 H 0 via the intermediate 3

2

3

0

3

3

3

4

3

2

2

2

Η—Ο—Ν—H H — Ν — Ο— Η The reaction might be concerted or could initially proceed by one fourcenter step in which one H 0 molecule was eliminated, followed by a second four-center step in which N and the other H 0 molecule were produced. The nitrogen-bearing products are produced from the ozonation of H N O . A possible sequence of steps is 2

2

HNO + 0 HN0

2

2

-> H N 0

3

2

+ 0

+ N H -> N H N 0 3

4

(11)

2

(12a)

2

-> N + 2 H 0 2

NH N0 4

2

+ 0

3

(12b)

2

-* NH4NO3 + 0

-> N 0 + 2 H 0 + 0 2

2

(13a)

2

2

(13b)

where Reactions 12b and 13 b are composite reactions. Alternately, H N 0 could react with 0

2

3

HN0

2

+ 0

-> H N O , + 0

3

HNO3 + N H

3

2

-> N H 4 N O 3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

(14) (15)

6.

207

Reaction of Ozone with Ammonia

OLSZYNA AND H E i C K L E N

The latter sequence does not produce N or N 0 . The competition between the two sequences may partially explain the increase i n [ N ] / [O ]o and [ N O ] / [ O ] at large [ N H ] / [ O ] . The reaction mechanism outlined above predicts that [ O ] / [ O ] should drop from 1.5 in the absence of N H to 1.0 for a long chain reaction in the presence of N H , which agrees well with the observations. The predicted value for [ H O ] / [ O ] is 0.25 + (2.25[N ] + 2 [ N 0 ] ) / [ O ] . The former quantity is 0.31 =h 0.03 in the absence of H e and 0.34 ± 0.02 in the presence of H e ; whereas the latter quantity is 0.38 ± 0.03 i n the absence of H e and 0.40 ± 0.03 in the presence of He. In both cases, the [ H 0 ] is low, probably because of losses by adsorption to the N H N 0 solid or the walls of the vacuum line. However, the discrepancy is not outside the experimental uncertainty. W i t h the steady state hypothesis for the reactive intermediates, Reactions 1-15 lead to the rate law 2

2

2

3

2

3

0

3

3

0

2

3

0

3

3

2

3

3

0

2

2

0

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

2

4

3

-^[Q ] dt 3

=

4 / ? W

ft [NH R& [0 ] + & [NH ] 4

+

i

3

3

3

4

3

where R is the rate of the initiation step, Reaction 1. In the above derivation Reaction 12b has been neglected. Including it complicates the expression and only reduces — d[O ~]/dt by about 1%. If the chain length is long, which is so since [ O ] / [ O ] •— 1.0, then Equation e simplifies to {

s

2

3

0

The expression for Ri is not obvious since the initiating reaction is a diffusion-inhibited wall reaction. Empirically, the form needed for Ri to fit the experimental observations for k is Ri = *i[O,]/([O,]

0

+ α[ΝΗ,]/β) (1 + γ[Ηβ])

(g)

with β = k k /16kik±k . In the absence of H e and at low values of [ N H ] / [ O ] , Equation g reduces to 3

3

3

2

10

7

0

Ri ^

fci[0,]/[0 ]o 8

(h)

This relationship suggests that the wall rate for some reason depends inversely on [ O ] . The rate constant k± in the packed cell, relative to that in the unpacked cell, is given by the inverse ratio of the correspond­ ing slopes in Figure 5. This value is 3.8 which compares with the i n ­ crease in surface to volume ratio of a factor of 3.4 when the cell is packed. As the [ N H ] / [ O ] ratio is increased, the relative importance of the 3

3

0

3

0

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

208

PHOTOCHEMICAL

SMOG A N D OZONE REACTIONS

interaction of N H with the surface increases, and the initiating rate law shifts to 3

Ri ^

fci[0,Wa[NH,]

The ratio α/β is the ratio of intercept to slope i n Figure 5 for the packed and unpacked cell. Since this ratio is larger in the packed cell, the influ­ ence of increasing [ N H ] / [ O ] is felt sooner i n the packed cell. W i t h H e added the other term i n Equation g reflects diffusional inhibition. This effect is more pronounced i n the unpacked cell as would be expected. However, the form of the term suggests that the diffusional effect is for N H , rather than 0 , diffusing to the wall. Otherwise the term should be (1 + γ [He] + γ ' [ Ν Η ] ). Regardless of the complexities of the wall initiation step, which are not well understood, Equation g can be substituted into Equation f to give a generalized rate law for long chains 3

3

0

3

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

(i)

3

3

-«[0,1^

dt r ιΓ

4 f r

0

71

3 j

M J N H , ] [OilAio

1

1 / 2

L (**[0,] + A; [NH ]) ([O,]o + «[NH,]/f) (1 + y[He]) J 4

3

The first prediction from Equation j is that the 0 decay is firstorder for h [ 0 ] > fc [NH ] and 3/2-order for fc [0 ] < fc [NH ]. W e have observed both rate laws and found that the cross-over occurs for [NH ]/[0 ] 100; consequently, fc /fc should be — 100. T h e rate constants k and fc have been measured. W e believe the best value (9) for k to be 5.2 X 1 0 M sec" at 30°C. The two most reliable results for fc are given by Albers et al. (10) and Kurylo et al. (11). Both of their Arrhenius expressions give the same value of 7.0 X MPM' sec" for k at 30°C. The ratio of these reported rate constants is 75, which supports our conclusion. It is a straightforward procedure to show that when fc [0 ] > > k [ N H ] Equation j reduces to a first-order rate law i n [ 0 ] with a rate constant which conforms to Equation c i n the absence of H e and E q u a tion d i n the presence of He. W e forced the form of Ri for this to be true; however forfc [ N H ] > > k [ 0 ] and H e absent, Equation j reduces to 3

3

3

4

3

3

3

3

s

3

4

3

4

4

6

3

_ 1

1

4

1

é

3

4

3

3

3

4

3

-d[Os]/dt ^

3

3

4Α: (Α; β/αΑ; ο[ΝΗ3]) [θ3] 7

1

1

1/2

(k)

3/2

This rate law is 3/2-order i n [ 0 ] as experimentally found and predicts that the 3/2-order rate constants, k', should vary as [ N H ] " . Figure 7 is a plot of (A:')" vs. [ N H ] i n the unpacked cell. The two values at the two highest N H pressures were omitted since they do not fit on the plot. The remaining data are scattered but they fit a straight line which passes through the origin. Some of the scatter can be attributed 3

3

2

1/2

3

3

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

1

6.

Reaction of Ozone with Ammonia

OLSZYNA AND HEICKLEN

209

to variation in the temperature among the runs. The slope of the line is 0.13 sq min. The ratio of this value to the intercept of Figure 5 (22 sq min) gives kjk$ = 0.006, which is about a factor of two lower than the ratio of 0.013 expected from literature values (See previous discussion). The reason for the discrepancy, as well as the failure of the two points at highest N H pressure to fit the plot, is uncertain, but the complications at the high N H pressures are severe: 1. The aerosol interferes with experimentally determining k' and probably accounts for the scatter. 2. The aerosol particles i n the gas phase can become centers for the heterogeneous reaction. 3. N H reacts readily with the surface at high N H pressures and thus continuously changes its nature throughout the run. 4. The diffusion effects become pronounced so that concentrations at the surfaces are different from those in the gas. This gradient in concentration not only affects the reaction rate but also affects the measured 0 concentration. Therefore the rate law is more complex than indicated by Equation k. Another complication is introduced at high pressures by the reaction 3

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

3

3

3

3

0 + 0

2

+ M—>0

8

+ M

which has a rate constant (12) of 2 X 1 0 M " sec" . This reaction should 8

2

1

20 r

Figure 7.

Flot of (k'Y vs. [NH ~\ for runs with [ N H ] / [O ] between 44-130 for the unpacked reaction cell 2

3

3

s

0

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.

210

PHOTOCHEMICAL SMOG AND OZONE REACTIONS

inhibit the rate as the reaction proceeds, the 0 becomes consumed, and 0 accumulates. The inhibition should have been apparent i n the pres­ ence of excess H e , but it was not. To prevent this difficulty, the reaction mechanism can be slightly altered if the 0 * produced i n Reaction 1 is assumed to be vibrationally excited 0 . Then Reactions 2, 3, and 4 are replaced by 3

2

2

2

0 * + 0 2

3

-> 0

2

+ 0

(30

3

0 * + N H —> H O + N H 0 3

2

(40

2

Downloaded by UNIV OF ARIZONA on November 28, 2012 | http://pubs.acs.org Publication Date: June 1, 1972 | doi: 10.1021/ba-1972-0113.ch006

The rate expression, Equation e, would become dt

~

6

K

i

+

4fc7lUsJ

L *.'[0,] +

fc '[NH ] 4

3

J

(e')

and the rest of the analysis would be unchanged. However, since the reaction order with respect to [ 0 ] is not changed by adding H e , this mechanism would require that H e be particularly inefficient in quenching 0 * . This alternative mechanism also has shortcomings because it is not clear why H e should be so inefficient. It is clear that initiation steps i n the 0 - N H reaction are not well understood. 3

2

3

3

Acknowledgment

W e wish to thank E . Lissi and W . B. DeMore for useful suggestions. This work was supported by the Environmental Protection Agency through the A i r Pollution Control Organization under Grant No. A P 00022, for which we are grateful. Literature Cited 1. Cohen, N., Heicklen, J., "Comprehensive Chemical Kinetics," Vol. 6, Else­ vier, in press. 2. Bacon, Η. E., Duncan, A. B. F.,J.Amer. Chem. Soc. (1934) 56, 336. 3. Strecker, W., Thienemann, H., Ber.Chem. Gesell (1920) 53, 2098. 4. Silverstein, R. M., Bassler, G. C., "Spectrometric Identification of Organic Compounds," p. 99, Wiley, New York, 1967. 5. Cusumano, J. Α., Low, M. J. D.,J.Phys. Chem. (1970) 74, 1950. 6. McGrath, W. D., Norrish, R. G. W., Proc. Roy. Soc. (London) (1960) A254, 317. 7. Olszyna, K. J., Heicklen, J.,J.Phys. Chem. (1970) 74, 4188. 8. Zipf, E. C., Can. J. Chem. (1969) 47, 1863. 9. Krezenski, D. C., Simonaitis, R., Heicklen, J., Int. J. Chem. Kinetics (1971) 3, 467. 10. Albers, Ε. Α., Hoyermann, K., Wagner, H. Gg., Wolfrum, J., Symp. Intern. Combust., 12th (1969) 313. 11. Kurylo, M. J., Hollinden, G. Α., LeFevre, H. F., Timmons, R. B.,J.Chem. Phys. (1969) 51, 4497. 12. Benson, S. W., DeMore, W. B., Ann. Rev. Phys. Chem. (1965) 16, 397. RECEIVED May 10, 1971.

In Photochemical Smog and Ozone Reactions; Advances in Chemistry; American Chemical Society: Washington, DC, 1972.